西安市秋冬季市区与山区微生物气溶胶组成特征及来源

为探究城市市区与山区微生物气溶胶组成特征及来源,在西安市市区(城区和郊区)及南郊山区设立3个采样点,采集细颗粒物、土壤及叶片样本.通过高通量测序法,解析不同采样点真菌与细菌群落结构,考察其时空变化特征;使用Source Track源解析技术对空气中微生物进行来源分析.结果表明,不同采样点真菌、细菌菌属差异较大,说明地理位置对空气中微生物的群落结构影响显著;冬季市区检测出较多的潜在真菌致病菌和细菌致病菌,且具有较高的相对丰度和多样性.通过源解析技术发现,在局部源叶片和土壤中,叶片表面微生物是空气中微生物的主要潜在源,且秋季叶片对空气中微生物的贡献率高于冬季.本研究不仅为空气中生物气溶胶的溯源研究提供了一定基础,也为深入了解大气中微生物污染特性和为我国空气环境质量评价与疾病预防提供一定的科学依据.     

白腐真菌GanodermaSinense对镉和蒽的去除能力

重金属和有机物复合污染是水处理中的难题。本研究发现一株白腐真菌Ganoderma Sinensis不仅可以通过富集作用去除重金属镉(Cd),而且对蒽具有降解能力。当Cd的浓度为10~30 mg/L时,该菌株对Cd的去除率为6.78%~21.9%;当蒽的浓度为10~30 mg/L时,菌株对蒽的降解率为18.25%~33.3%;当Cd和蒽同时存在于培养基中时,随着Cd浓度的增加(10~30 mg/L),对菌株的生物量及蒽降解的抑制作用也在增大;而随着蒽浓度的增加(10~30 mg/L),菌株的生物量及Cd的富集能力并未受到显著的影响。实验结果表明,该菌株有望用于镉和蒽复合污染的水体处理。     

白腐真菌生物降解TNT装药废水的研究

本文利用自行培养驯化的白腐真菌，对实际ＴＮＴ装药废水进行了好氧生物降解实验。结果表明，经过五天时间的降解，废水中所含的主要成分ＴＮＴ接近完全降解，效果非常显著。对实验所获得时间序列进行动力学研究，结果证明了白腐真菌降解ＴＮＴ的反应为准一级动力学反应     

The Role of Fungal Symbioses in the Adaptation of Plants to High Stress Environments

All plants studied in natural ecosystemsare symbiotic with fungi that either resideentirely (endophytes) or partially(mycorrhizae) within plants. Thesesymbioses appear to adapt to biotic andabiotic stresses and may be responsible forthe survival of both plant hosts and fungalsymbionts in high stress habitats. Here wedescribe the role of symbiotic fungi inplant stress tolerance and present astrategy based on adaptive symbiosis topotentially mitigate the impacts of globalchange on plant communities.     

Arbuscular mycorrhizal fungi, rhizobia, available soil P and nodulation of groundnut (Arachis hypogaea) in Zimbabwe

Arbuscular mycorrhizal fungal (AMF) colonization and nodulation of groundnut were examined in nine soils collected from subsistence farmers’ fields in Zimbabwe. Nodule number, shoot dry weight, shoot N and P contents, and AMF colonization were assessed after 6 weeks growth. Both nodule number and AMF colonization differed by an order of magnitude among the nine soils. Soil available P explained almost all the variability in nodule number (r² = 0.98), but had no significant effect on percent AMF colonization. By adding P to one soil, nodule numbers increased four-fold resulting in a significantly higher N content in the shoots. Similar, but smaller, effects were obtained by increasing the abundance of AMF through an inoculation with Glomus intraradices, suggesting that nodulation in this soil was limited by AMF abundance and that the fungi could, to a limited extent, substitute for P fertilizer.     

To enhance the reproduction of Phanerochaete chrysosporium by adding natural lixiviums in liquid medium

Great promotion to the reproduction of white rot fungus Phanerochaete chrysosporlum by adding natural lixiviums such as from wood, maize core and potato in liquid medium was found in this research. Incubated in the liquid medium contained 10 mg/L glucose as carbon source with natural lixiviums for three days, the production of myeelium pellet reaches more than 80 g/L, which is 5 times more than that of without natural lixiviums. Incubated in the liquid medium contained 5 mg/L glucose as carbon source with natural lixiviums for three days, the production of myeelium pellet can reach 69.5 g/L, while the production in the medium without natural lixiviums is very low. When the liquid medium contained 1-20 g/L glucose as carbon source, the production of myeelium pellet in 3 d can only reach 12.5 g/L to 14.5 g/L. The fungus in the medium with potato lixiviums are easily contaminated by other microorganisms and in the medium with maize core lixiviums are easily bulking, while in the medium with wood lixiviums are neither easily contaminated nor bulking. Medium with wood lixiviums can produce more pellet than other medium, endure contamination and keep better sedimentation capacity. So that, wood lixivium is borer additive to the culture of white rot fungi in liquid medium. Addition of the mixture of wood, maize core and potato lixiviums is of advantage to the productian of mycelium pellet. The difference of the production in the medium with different amount of wood lixiviums showed little in the first 3 d, while it esnanded after 3 d. Wood lixiviums stimulate the growth of P. chrysosporium instead of supply organies which fungi need.     

白腐真菌对土壤中多环芳烃(PAHs)降解的研究

研究白腐真菌对多环芳烃(PAHs)的降解,结果表明,温度、培养基、氧气浓度、水土比对PAHs的降解均有影响.温度为25℃、营养液为查氏培养基、通气量为60L·d-1、水土比为5∶1为最优水平组合.对降解不同时期各种因素的重要性及其最优水平的分析表明,各种影响因素在降解实验的不同阶段的影响程度不同,降解实验初期,培养基是最重要的影响因素,而氧气在整个实验中均为重要的影响因素.     

土壤中酞酸酯(PAEs)对丛枝菌根化植物生长的影响

以豇豆 (Vignaunguiculata )为供试植物 ,分别接种AM真菌Acaulosporalavis(光壁无梗球囊霉 ,菌号 :3 4)和Glomuscaledonium (苏格兰球囊霉 ,菌号 :90 0 3 6) ,通过温室盆栽试验 ,观察 2、10和 5 0mg·kg-1DEHP和DBP对菌根化植物生长的影响。试验结果表明 ,土壤添加DEHP和DBP后 ,植物地上和地下部分干重均有不同程度下降 ,高浓度DEHP和DBP还使植物叶绿素a和b的含量及根瘤数降低 ,接种AM真菌后明显促进了植物的生长 ,尤其对植物早期地下部分和植物后期地上部分的促进作用较为明显 ;同时 ,也增加了植物叶绿素a和b的含量及根瘤数     

白腐菌在固体培养基下对吲哚和吡啶的降解

研究了稻草秆粉介质中白腐菌对吲哚和吡啶的降解.实验结果表明,质量浓度分别为200、80 mg/L左右的吲哚可被白腐菌去除99%以上,质量浓度为74 mg/L吡啶的去除率为61.5%;白腐菌在稻草秆粉培养体系中对吲哚和吡啶的降解,符合零级反应动力学,其中反应速率常数K(高浓度吲哚)＞K(低浓度吲哚)＞K(吡啶);高低浓度吲哚和吡啶3个降解体系的漆酶活力在第6天达到最大;漆酶在吲哚和吡啶降解过程中起着较重要的作用,但酶活的变化与吲哚和吡啶的相对去除率不呈线性相关,稻草秆粉培养基中的介质和培养环境在降解过程中可能也起着重要作用.     

Degradation of Benzo[a]Pyrene in Soil with Arbuscular Mycorrhizal Alfalfa

Mycorrhizal and non-mycorrhizal alfalfa (Medicago sativa) was grown in pots containing soil artificially contaminated with various levels of benzo[a]pyrene (B[a]P)(0, 1, 10 and 100 mg kg^–1). Soil and plants were sampled after 30, 40, 50, 60 and 90 days and compared with unlanted pots. The percentage of mycorrhizal root length colonized by Glomus caledoniun was not significantly affected by the addition of B[a]P up to 10 mg kg^–1 but was significantly lower at 100 mg kg^–1B[a]P compared with low concentrations (p < 0.05). There was no difference in soil polyphenol oxidase and dehydrogenase activity among the controls and applications of 1 and 10 mg kg^–1 of B[a]P. However, enzyme activities were significantly higher at 100 mg kg^–1B[a]P compared with the other three treatments, and there was no mycorrhizal effect. Over a period of 90 days the concentration of B[a]P in soil in which alfalfa was grown was significantly lower than in unplanted soil (p < 0.05). Degradation rates of B[a]P added at 1, 10 and 100 mg kg^–1 without G. caledonium were 76, 78 and 53%, and with mycorrhizal inoculation were 86, 87 and 57%. The degradation rate in unplanted soil was significantly lower than in planted soil, and was significantly higher in medium- and low-B[a]P treatments than in the high B[a]P concentration tested. There is a possibility of enhancement phytoremediation of PAHs in rhizosphere soil with arbuscular mycorrhizal fungi.